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The Conservation of the Endemic Vascular Flora of Ascension Island and Threats from Alien Species

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The Conservation of the Endemic Vascular Flora of Ascension Island and Threats from Alien Species Oryx Vol 39 No 4 October 2005 Short Communication The conservation of the endemic vascular flora of Ascension Island and threats from alien species Alan Gray, Tara Pelembe and Stedson Stroud Abstract We present the first assessment of the purpurascens, A. ascensionis, and X. ascensionensis appear endemic vascular flora of Ascension Island for over to be under no immediate threat of extinction, although 20 years. Combining new with existing data the follow- long-term survival is uncertain. E. origanoides, P. adscen- ing IUCN Red List categorizations are proposed: sionis, and S. caespitosus require active conservation Anogramma ascensionis, Dryopteris ascensionis, Oldenlandia measures to ensure their survival. adscensionis and Sporobolus durus (Extinct); Pteris adscen- sionis and Euphorbia origanoides (Critically Endangered); Keywords Sporobolus caespitosus (Vulnerable); Asplenium ascensionis, Ascension Island, exotic species, flora, Red Marattia purpurascens and Xiphopteris ascensionensis (Near List. Threatened). The primary cause of the four presumed extinctions appears to be introductions of exotic species This paper contains supplementary material that can and subsequent alteration of ecological conditions. M. only be found online at http://journals.cambridge.org Ascension Island (97 km2) is a volcanic island in the is often shrouded in mist and a high proportion of the South Atlantic Ocean (7°57’S, 14°22’W). Its closest neigh- rainfall is in the form of occult deposition. The low-lying bour is St Helena 1,127 km to the south. Approximately lava plains exhibit xeric conditions common to many 1 million years old (Nielson & Sibbett, 1996), a distinctive desert habitats, and higher areas on the lava plains, such flora has evolved on Ascension, in common with many as Sisters Peak, remain dry for much of the time. other oceanic islands. The last Red List assessment of the Studer (1889 cited in Duffey, 1962) distinguished three vascular flora of Ascension (Cronk, 1980) concluded that vegetation zones, elaborated by Duffey (1962). Although of the 10 endemic species, 1 was Extinct, 5 Endangered the details have changed since the visits of both Studer and 4 Rare. The principal cause of the extinction and and Duffey, indicating Ascension’s vegetation ecology threats were 19th century introductions of exotic species to be in a state of flux, the zones remain useful for (Cronk, 1980). As the island is still in a state of ecological descriptive purposes. flux, a reassessment of the Red List status of the flora is Zone 1 Dry area below 330 m. Similar to Duffey’s long overdue. description, with patchy but often extensive vegetation, The climate of Ascension largely reflects its altitudinal especially after rain, with species including the endemic gradient but is modified by the south-east trade winds Euphorbia origanoides L., the native Aristida adscensionis (Duffey, 1964). On the coast at Georgetown temperatures L. and Cyperus appendiculatus Kunth, and the introduced are 27–31°C and mean annual rainfall c. 140 mm; tem- Enneapogon cenchroides (Licht.) C.E.Hubb., Argemone peratures at 660 m on Green Mountain are 6°C lower than at Georgetown and mean annual rainfall is mexicanca L., Heliotropium sp., Nicotiana glauca R.Grah., c. 680 mm (Ashmole & Ashmole, 2000). Green Mountain and Waltheria indica L.. The most notable change is the addition of Prosopis juliflora (Sw.) DC., which dominates large areas and has displaced much of the Acacia scrub Alan Gray (Corresponding author) Ecology and Resource Management, described by Duffey. School of GeoSciences, University of Edinburgh, Darwin Building, The King’s Buildings, Mayfield Road, Edinburgh, EH9 3JU, UK. Zone 2 Between 330 and 660 m. A more complete E-mail [email protected] coverage of vegetation with patchy mosaics of P. juliflora, Juniperus bermudiana L., Causurina equisetifolia L., Tecoma Tara Pelembe and Stedson Stroud Ascension Island Conservation, Conservation Centre, Georgetown, Ascension Island, ASCN IZZ, stans (L.) H.B. & K., Opuntia sp., Leucaena leucocephala South Atlantic Ocean. (Lam.) de Wit, Lantana camara L., N. glauca, Psidium Received 15 June 2004. Revision requested 4 November 2004. guajava L., and Acacia spp.. This is the zone where the Accepted 13 April 2005. grass Melinis minutiflora attains its highest abundance. © 2005 FFI, Oryx, 39(4), 449–453 doi:10.1017/S0030605305001092 Printed in the United Kingdom 449 Downloaded from https://www.cambridge.org/core. IP address: 170.106.35.229, on 25 Sep 2021 at 20:46:44, subject to the Cambridge Core terms of use, available at https://www.cambridge.org/core/terms. https://doi.org/10.1017/S0030605305001092 450 A. Gray et al. Zone 3 Mist region from 660 to 850 m. This zone has Ascension are to expand their range, some control will been erroneously described as rainforest (Pearce, 2004). be required for all the severe threat species. The vegetation forms an almost complete cover made up Little is currently known about the biology and of a mosaic of grassland, scrub, woodland, bamboo (on ecology of the endemic species. Studies on the flora the summit) and ginger. Species in this mosaic include have been sporadic (Duffey 1964; Cronk, 1980; Gray et al., Alpinia zerumbet (Pers.) B.L.Burtt & R.M.Smith, Bambusa 2000) and have concentrated on distribution rather than sp., J. bermudiana I spp., Sporobolus africanus (Poir.) ecology or practical conservation. Although an ecological Robyns & Tournay, and Paspalum spp. investigation of E. origanoides was commissioned in 2003 Further details of the physical characteristics of Ascen- there are currently, to our knowledge, no plans to repeat sion Island are provided by Duffey (1964) and Ashmole this type of work for any of the other endemics. Details of & Ashmole (2000), and fuller discussions of flora, ecology the population dynamics of the endemics is limited to and conservation by Duffey (1964), Cronk (1980, 2000), anecdotal information. The estimated total area covered Packer & Packer (1997), Ashmole & Ashmole (2000), by populations of endemic species in 2003 appears to be Gray et al. (2000) and Gray (2003). greater than that given by Cronk (1980), but although Here we examine the threats to the flora of Ascension this may represent a real increase it could also reflect the (Gray, 2004; Wilkinson, 2004) and reassess the Red List greater recording effort of later surveys. It is difficult status of the endemic species (Walter & Gillet, 1998) to assess population dynamics without consistent and using the most recent criteria (IUCN, 2001). There is no standardized monitoring. All endemic populations are plant checklist for Ascension and taxonomic nomencla- localized and fragmented and, in the case of P. adscen- ture therefore follows Cronk (1980, 2000). The histori- sionis, there are few individuals remaining (Table 1). cally recorded sites of all the endemic vascular plants The best information available for any population is were surveyed in 1998, 2002 and 2003, and with a brief for E. origanoides. The increase in area occupied by the visit in November 2004 to assess E. origanoides. Survey species from 1958 (50 ha) to 1976 (75 ha) was in part work was broadened in 2002 and 2003, covering almost because of the appearance of a new population at South all of the island with the exception of inaccessible cliffs. Gannet Hill, now holding c. 90% of the island population. This provided estimates of population size and island The decrease from 1976 to 1998 (20 ha) seems to have distribution, and recorded any threats, including evi- been a combination of the loss of the English Bay popula- dence of habitat change and associated alien species. tion because of construction work and the effects of drier Introduced species that are capable of displacing an weather conditions. The rise from 1998 to 2003 (24 ha) endemic by dominating a particular site and altering eco- coincided with wetter climatic conditions (192 mm in logical conditions, such as light, nutrients and moisture 2003 compared to 97 mm in 1998). Population fluctua- availability, were categorized as severe threat species tions seem to be characteristic of this species, partly (Table 2). This was done with reference to a range of accounted for by rainfall events (Gray, 2003). A previ- sources but all are included in the SEPASAL database ously unrecorded population of c. 1,000 individuals near (Royal Botanic Gardens, Kew 1999), Cronk & Fuller Wig Hill was recorded in 2003. This is important because (2000) and Weber (2003). the population at South Gannet Hill suffered a 50% The flora of Ascension comprises c. 25 native vascular reduction (pers. obs., November 2004), perhaps because plants of which 10 are endemic (Cronk, 1980) (Table 1), and c. 280 introduced species (Appendices 1–2). Many of expansion of the rabbit population following feral cat introduced species are present at locations that have control; recent analysis of rabbit faeces found fragments endemics (Table 1), and most of these sites contain severe of E. origanoides (pers. obs., November 2004). threat species (Table 2). Of the 13 severe threat species, The most significant change in Red List status is the P. juliflora represents a threat not only to native plants categorization of Sporobolus durus, Dryopteris ascensionis but also to turtle nesting beaches (Fowler, 1998; Pickup, and Anogramma ascensionis as Extinct (Table 1). The only 1999). Control of this species has been discussed else- places where they could still exist would be in a remote where (Fowler, 1998) but the future of E. origanoides ravine or on a cliff face. Reported sightings of D. (especially for any restoration projects) may depend on ascensionis (1975) and O. adscensionis (in the 1980s) remain the extermination of P. juliflora in specific areas and unconfirmed (Cronk, 1980, 2000). The categories of Asple- containment of the feral sheep and donkey populations nium ascensionis, Marattia purpurascens and Xiphopteris that disperse seeds. Goats have also been implicated in ascensionensis are unchanged as their populations appear the extinction of at least one endemic species, Oldenlandia to be large enough for survival, at least in the short-term.
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